US7521035B1 - Method for regenerating a residual substance that contains sulfur and an atomizing burner suited for carrying out said method - Google Patents

Method for regenerating a residual substance that contains sulfur and an atomizing burner suited for carrying out said method Download PDF

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US7521035B1
US7521035B1 US10/380,386 US38038601A US7521035B1 US 7521035 B1 US7521035 B1 US 7521035B1 US 38038601 A US38038601 A US 38038601A US 7521035 B1 US7521035 B1 US 7521035B1
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Prior art keywords
residue
oxygen
gas stream
nozzle
reaction zone
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English (en)
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Gerhard Grob
Heinz Gruning
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Messer Griesheim GmbH
Air Liquide Deutschland GmbH
Roehm GmbH Darmstadt
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Messer Griesheim GmbH
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Assigned to MESSER GRIESHEIM GMBH, ROEHM GMBH & CO. KG reassignment MESSER GRIESHEIM GMBH ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: GROB, GERHARD, DR., GRUNIG, HEINZ, DR.
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    • C—CHEMISTRY; METALLURGY
    • C01—INORGANIC CHEMISTRY
    • C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00—Sulfur; Compounds thereof
    • C01B17/48—Sulfur dioxide; Sulfurous acid
    • C01B17/50—Preparation of sulfur dioxide
    • C01B17/58—Recovery of sulfur dioxide from acid tar or the like or from any waste sulfuric acid
    • C01B17/585—Recovery of sulfur dioxide from acid tar or the like or from any waste sulfuric acid from ammonium sulfate containing sulfuric acid solutions
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
    • F23G5/14—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23D—BURNERS
    • F23D2212/00—Burner material specifications
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23D—BURNERS
    • F23D2214/00—Cooling
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23D—BURNERS
    • F23D2900/00—Special features of, or arrangements for burners using fluid fuels or solid fuels suspended in a carrier gas
    • F23D2900/00006—Liquid fuel burners using pure oxygen or oxygen-enriched air as oxidant
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23D—BURNERS
    • F23D2900/00—Special features of, or arrangements for burners using fluid fuels or solid fuels suspended in a carrier gas
    • F23D2900/00018—Means for protecting parts of the burner, e.g. ceramic lining outside of the flame tube
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2202/00—Combustion
    • F23G2202/10—Combustion in two or more stages
    • F23G2202/101—Combustion in two or more stages with controlled oxidant supply
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2202/00—Combustion
    • F23G2202/10—Combustion in two or more stages
    • F23G2202/102—Combustion in two or more stages with supplementary heating
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2209/00—Specific waste
    • F23G2209/10—Liquid waste
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2209/00—Specific waste
    • F23G2209/12—Sludge, slurries or mixtures of liquids
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2900/00—Special features of, or arrangements for incinerators
    • F23G2900/54402—Injecting fluid waste into incinerator
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00—Combustion technologies with mitigation potential
    • Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00—Technologies relating to chemical industry
    • Y02P20/10—Process efficiency
    • Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

Definitions

  • the present invention relates to a method for the regeneration of residues containing sulfur in that a droplet stream containing the residue is introduced into a reactor and fed to a reaction zone consisting of hot flue gases that are generated by the combustion of a fuel, and heated in said reaction zone so that the compounds of the residues containing sulfur are thermally cleaved.
  • the invention relates to an atomizing burner for executing the method, comprising a central inner nozzle that serves to feed in the residues containing sulfur and that is surrounded by an outer nozzle.
  • residues containing sulfur such as, for example, spent sulfuric acids (so-called “waste sulfuric acids”) or ammonia sulfate solutions, are treated by means of thermal cleavage in so-called cleaving installations.
  • the residues are fed into a heating zone of a reactor with a refractory lining, hereinafter referred to as a “cleaving oven”, said heating zone being created by hot flue gases, where these residues are thermally cleaved under formation of sulfur dioxide.
  • the heating zone is created by burning a fuel with an oxidant that contains oxygen.
  • the process gases containing sulfur dioxide are further processed according to the state of the art into sulfuric acid, fuming sulfuric acid or sulfur dioxide.
  • reactors Two different types of reactors are commonly used, which differ primarily in terms of the process gas flow, namely, cleaving ovens with a vertical or with a horizontal flow.
  • the burners for generating the hot flue gases are flanged directly onto the oven wall radially or tangentially in one or more planes.
  • the flame first develops in the cleaving oven, whereby CO and soot might form as a result of incomplete combustion, and there is a risk that the sulfuric acid produced could acquire a brown coloration. Therefore, the more modern cleaving installations are equipped with upstream combustion chambers, called combustors, rather than with the directly flanged-on burners. Combustors generate a hot, fully reacted flue gas at a temperature of about 2000° C. [3632° F.].
  • one or more burners or combustors are flanged directly onto the end wall.
  • the flame or the flue gas exit horizontally.
  • Examples of possible fuels are combustible gases and liquid fuels, preferably with a high sulfur content, such as, for example, fuel oil. If there is a need to increase the sulfuric acid production, liquid sulfur is also added as the fuel, and it burns directly in the cleaving oven to form sulfur dioxide.
  • the oxidation medium normally used is air, which is either added to the burner box at the ambient temperature or else recuperatively heated.
  • the acid is fed into the cleaving oven by means of pressure atomizers, compressed-air atomizers or rotary atomizers that are made of acid-proof materials.
  • All cleavage methods have in common the requisite very high cleavage temperature of 900° C. to 1200° C. [1652° F. to 2192° F.] at which the residues containing sulfur are converted into sulfur dioxide, water vapor, oxygen and optionally nitrogen and carbon dioxide.
  • the strong endothermic cleavage reaction takes place in the cleaving ovens described above, requiring large amounts of energy in the form of combustible gas or oil.
  • about 1770 KWh of energy per ton of waste acid are needed for the cleavage of a 70%-solution of waste sulfuric acid, consisting of 70% sulfuric acid and 30% water.
  • the inert nitrogen fraction When air is used as the oxidant, the inert nitrogen fraction also has to be heated to the cleavage temperature of about 1000° C. [1832° F.], thus additionally raising the energy consumption and reducing the sulfur dioxide concentration as well as increasing the process gas volume.
  • Higher sulfur dioxide concentrations can be achieved either by concentrating the residues containing sulfur in a separate installation or by reducing the inert nitrogen fraction in the combustion air, which is normally achieved by using oxygen as the oxidation medium.
  • fuels such as oil or combustible gas are burned by means of a suitable burner, while being mixed externally with oxygen.
  • the oxygen burners can additionally be integrated into the reactor so as to improve the performance of an existing cleaving oven, or else to replace air burners.
  • the very high flame temperatures of up to 2900° C. [5252° F.] give rise to the same problems as with the previously mentioned methods.
  • water-cooled oxygen burners are maintenance-intensive since corrosion damage can occur on the cooled surfaces due to the condensation of sulfuric acid.
  • the present invention is based on the objective of providing a method for the regeneration of residues containing sulfur in which oxygen can be introduced into the cleavage oven without the above-mentioned drawbacks and limitations as an additional oxidation medium in order to enhance the performance and improve the cost-effectiveness. Moreover, the invention is based on the objective of providing a suitable atomizing burner with a long service life for executing the process.
  • this objective is achieved according to the invention in that a droplet stream containing fuel is fed into the reactor simultaneously with the droplet stream containing the residue, and is introduced into a pre-reaction zone that is created by feeding in an oxygen-rich gas stream, whereby the residue in the pre-reaction zone is partially thermally cleaved and subsequently fed into the reaction zone.
  • the droplet stream containing the residue and the droplet stream containing the fuel are fed into a pre-reaction zone.
  • This zone is created in that finely distributed residue and fuel react with the oxygen-rich gas.
  • the residue containing sulfur is partially cleaved and subsequently fed into the reaction zone having a higher temperature and consisting of the hot flue gases.
  • the pre-reaction zone is thus separate from the actual reaction zone.
  • the pre-reaction zone is created in that fuel is burned there with the oxygen-rich gas stream.
  • the fuels for forming the pre-reaction zone and the actual reaction zone can be identical.
  • the oxygen-rich gas stream consists of pure oxygen or of an oxygen-air mixture with an oxygen concentration between 25 vol.-% and 100 vol.-%.
  • the thermal cleavage of the residue can be carried out in the actual reaction zone at low reaction temperatures, which translates into a low formation of nitrogen oxide at high reaction rates in the overall process.
  • the reaction products from the pre-reaction zone that had not yet been completely cleaved are transferred to the actual reaction zone having a higher temperature, where the complete cleavage and combustion of the reaction products takes place without the additional formation of nitrogen oxide.
  • a maximum temperature in the range between 800° C. and 1300° C. [1472° F. and 2372° F.], especially preferred between 850° C. and 1100° C. [1562° F. and 2012° F.], is set in the pre-reaction zone.
  • the temperature in the pre-reaction zone can be regulated by separately setting the volume flows of the residue containing sulfur, the fuel and the oxygen-rich gas. These are set independently of each other in such a way that the temperature in the pre-reaction zone lies within the above-mentioned preferred temperature ranges.
  • a reducing atmosphere is maintained in the first reaction zone in that the oxygen content in the pre-reaction zone is set sub-stoichiometrically with respect to the oxidizable components of the residue and of the fuel.
  • atomizing medium here is defined as the media that are supplied to the atomizer and that directly or indirectly contribute to the atomization of the residue and the fuel. In particular, this also refers to such media that are supplied to the atomizer with the objective of surrounding the atomization cone that is forming during the atomization. Pressure atomizers, rotary atomizers or injector atomizers are used as the atomizers.
  • a residue-fuel mixture in the form of residue-fuel droplet stream is fed into the reactor.
  • the residue-fuel mixture is created outside of the reactor.
  • This mixture is supplied to an atomizer in order to form the residue-fuel droplet stream and then the mixture is introduced into the pre-reaction zone by the atomizer.
  • the oxygen-rich gas stream is fed into the pre-reaction zone together with this mixture or else separately.
  • the oxygen-rich gas stream it is especially advantageous for the oxygen-rich gas stream to surround and penetrate the residue-fuel droplet stream as a sheathing gas stream, thus creating the first reaction zone.
  • the sheathing gas stream in this context is completely or partially formed by the oxygen-rich gas stream or by part thereof.
  • the sheathing gas stream is also advantageously used partially or entirely as the secondary atomizing medium for the residue-fuel mixture.
  • a configuration of the method according to the invention that has especially proven its worth is one in which the sheathing gas stream is partially made up of an air stream, whereby the oxygen content in the sheathing gas stream is set between 25 vol.-% and 100 vol.-%.
  • the oxygen content in the sheathing gas stream is set as a function of the ratio of the flow volumes of the air stream to the oxygen-rich gas stream and its oxygen content.
  • an atomizing burner having a central inner nozzle that feeds in the residue-fuel mixture and that is coaxially surrounded by an inert gas nozzle and by a ring-shaped nozzle that feeds the oxygen-rich sheathing gas stream, whereby inert gas is fed through the inert gas nozzle.
  • the inert gas fed through the inert gas nozzle serves to protect the central inner nozzle from the oxygen-rich sheathing gas stream. Consequently, the inner nozzle can be made of a material that would oxidize readily at the prevailing high temperatures if it comes into contact with the oxygen-rich sheathing gas stream.
  • the oxygen-rich gas stream comprises a pre-heated hot air stream and an oxygen-rich gas stream that is handled separately from it.
  • the oxygen content of the oxygen-rich gas stream is preferably at least 80 vol.-%.
  • the objective set forth is achieved according to the invention in that, between the inner nozzle and the outer nozzle, there is an inert gas nozzle that coaxially surrounds the inner nozzle, and in that the inner nozzle is connected to an inlet for a residue-fuel mixture and the outer nozzle is connected to an inlet for an oxygen-rich gas stream.
  • an inert gas nozzle between the inner nozzle and the outer nozzle.
  • the inert gas nozzle surrounds the inner nozzle coaxially.
  • an inert gas can be fed in through the inert gas nozzle, whereby said inert gas is inert vis-à-vis the inner nozzle and it protects the inner nozzle from the outside environment.
  • This means that it is it possible to make the inner nozzle out of a material that is resistant to the residues containing sulfur, but that is not stable vis-à-vis the medium coming out of the outer nozzle.
  • the inner nozzle is connected to an inlet for a residue-fuel mixture
  • the outer nozzle is connected to an inlet for an oxygen-rich gas stream.
  • the oxygen-rich gas stream as set forth in the present invention has an oxygen content between 25 vol.-% and 100 vol.-%.
  • the atomizing burner according to the invention makes it possible to atomize the residue while feeding in an oxygen-rich gas stream or a part thereof through the outer nozzle, whereby the inner nozzle can be protected from the oxygen-rich gas stream by feeding in a suitable inert gas through the inert gas nozzle. Consequently, the inner nozzle can be made of a material that would otherwise be susceptible to corrosion under the ambient conditions.
  • the inner nozzle is made of zirconium.
  • Zirconium stands out for its high acid resistance and durability, but at high temperatures (for example, at 1000° C. [1832° F.]), due to its affinity, it oxidizes readily or might even be ignited in pure oxygen, which is prevented by the medium fed in through the inert gas nozzle.
  • Another improvement of the atomizing burner according to the invention consists in that there are swirling devices in the outer nozzle.
  • the swirling devices bring about an additional secondary atomization of the residue-fuel mixture.
  • An especially simple embodiment of the atomizing burner is one in which the outer nozzle is configured as an annular gap that coaxially surrounds the inert gas nozzle.
  • the outer nozzle is configured as an annular gap in which a plurality of individual nozzles are distributed along the outer perimeter of the inert gas nozzle.
  • a first gas can be fed in through the annular gap and a second gas through the individual nozzles.
  • the first gas can be preheated air and the second gas can be an oxygen-rich gas stream as set forth in this invention, having an oxygen content of preferably at least 80 vol.-%.
  • FIG. 1 the atomizing burner according to the invention in a first embodiment
  • FIG. 2 the atomizing burner according to FIG. 1 in a top view of the opening of the atomizing nozzle
  • FIG. 3 a second embodiment of the atomizing burner according to the invention having an outer nozzle fitted with a swirling device
  • FIG. 4 the atomizing burner according to FIG. 3 in a top view of the opening of the atomizing nozzle
  • FIG. 5 a third embodiment of the atomizing burner according to the invention having an outer nozzle with individual nozzles arranged therein, and
  • FIG. 6 the atomizing burner according to FIG. 5 in a top view of the opening of the atomizing nozzle.
  • the atomizing burner shown in FIG. 1 has a central inner nozzle 1 that is coaxially surrounded by a ring-shaped gas separation nozzle 2 and by another ring-shaped outer nozzle 3 .
  • the inner nozzle 1 has an inlet 4 for a mixture of residues containing sulfur and fuel such as, for example, light oil or heavy fuel oil, waste oil or solvent, the gas separation nozzle 2 is provided with an air inlet 5 and the outer nozzle 3 is provided with an inlet 6 for an oxygen-air mixture whose oxygen content can be varied between 20.6 vol.-% and 100 vol.-%.
  • the inner nozzle is formed by a tube 8 made of zirconium that is tapered conically in the direction of the nozzle opening 7 .
  • the remaining walls of the nozzles ( 2 ; 3 ) consists of heat-proof, sulfur-resistant, high-alloy stainless steel in the form of two coaxial tubes ( 9 ; 10 ).
  • the top view of the atomizing burner according to FIG. 2 shows the coaxial arrangement of the individual tubes ( 8 ; 9 ; 10 ) and of the nozzles ( 1 , 2 , 3 ) of the atomizing burner according to FIG. 1 .
  • the top view of the atomizing burner according to FIG. 4 shows the coaxial arrangement of the individual tubes ( 8 ; 9 ; 10 ) and of the nozzles ( 1 , 2 , 3 ) as well as the lamellae 12 inside the outer nozzle 3 of the atomizing burner according to FIG. 3 .
  • FIG. 5 shows an embodiment of the atomizing burner according to the invention in which, inside the ring-shaped outer nozzle 3 , a plurality of individual nozzles 14 (in the embodiment, there are eight individual nozzles 14 ) are arranged in a circular cross section.
  • the individual nozzles 14 are uniformly distributed around the gas separation nozzle 2 . They consist of tubes made of austenitic material whose upper end facing away from the nozzle opening 7 is connected to an oxygen inlet 15 .
  • the outer nozzle 3 is connected to an inlet 16 for hot air.
  • the oxygen is separated from the preheated oxygen-air mixture until the nozzle opening 7 . In this manner, any desired amount of oxygen or air can be safely fed into the oven.
  • the top view of the opening of the atomizing nozzle according to FIG. 6 shows the coaxial arrangement of the individual tubes ( 8 ; 9 ; 10 ) and of the nozzles ( 1 , 2 , 3 ) as well as the arrangement of the circular individual nozzles 14 around the gas separation nozzle 2 in the atomizing burner according to FIG. 5 .
  • an existing cleaving installation having a cleaving oven with a vertical flow is used; here, the residues are injected at the oven head and the process gas flows through the cleaving oven from the top to the bottom.
  • the cleaving oven is fired with heavy fuel oil S as the fuel and pre-heated air as the oxidation medium by means of two tangentially arranged combustors.
  • the residue that is injected from the top by the atomizing nozzle is thermally cleaved in the hot flue gases generated by the combustors.
  • the residue used was 12 m 3 /h of a waste acid from the production of methyl methacrylate having the following composition:
  • the atomization is carried out with a conventional atomizing nozzle.
  • the fed-in residue quantity of 12 m 3 /h corresponds to the maximum capacity of the installation.
  • the results achieved are compiled in bulleted form below.
  • Example 3 with the same composition of the residue as in Example 1, the throughput rate of residue containing sulfur was increased by 33.3%, from 12 m 3 /h to 16 m 3 /h.
  • the oxygen volume was 2000 m 3 /h.
  • the energy needed for the additional cleavage was fed via the atomizing burner according to the invention, which is shown in FIGS. 1 and 2 , by admixing 510 kg/h of heavy heating oil S with the residue containing sulfur and introduced into the pre-reaction zone.
  • the degree of cleavage was only slightly higher, as can be seen on the basis of the SO 3 values. No increase in the temperature at the oven head was observed.
  • the temperature at the cleaving oven outlet was constant.
  • the method is suitable for enhancing the performance of existing cleaving installations as well as for reducing the installation size when new installations are built.

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Inorganic Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Pharmaceuticals Containing Other Organic And Inorganic Compounds (AREA)
  • Treating Waste Gases (AREA)
  • Physical Or Chemical Processes And Apparatus (AREA)
US10/380,386 2000-09-12 2001-09-07 Method for regenerating a residual substance that contains sulfur and an atomizing burner suited for carrying out said method Expired - Fee Related US7521035B1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE10045320A DE10045320A1 (de) 2000-09-12 2000-09-12 Verfahren zur Regenerierung von schwefelhaltigem Reststoff und zur Durchführung des Verfahrens geeigneter Zerstäubungsbrenner
PCT/EP2001/010346 WO2002023088A1 (de) 2000-09-12 2001-09-07 Verfahren zur regenerierung von schwefelhaltigem reststoff und zur durchführung des verfahrens geeigneter zerstäubungsbrenner

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US7521035B1 true US7521035B1 (en) 2009-04-21

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US (1) US7521035B1 (de)
EP (1) EP1319151B1 (de)
AT (1) ATE287513T1 (de)
AU (1) AU2002210493A1 (de)
CA (1) CA2434343C (de)
DE (2) DE10045320A1 (de)
ES (1) ES2236318T3 (de)
WO (1) WO2002023088A1 (de)

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EP4415885B1 (de) 2021-10-11 2025-11-05 Basf Se Zerstäuberdüse

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4062657A (en) * 1975-05-09 1977-12-13 Eisenwerk-Gesellschaft Maximilianshutte Mbh Method and apparatus for desulphurizing in the gasification of coal
US4827486A (en) * 1986-08-27 1989-05-02 Klockner Cra Technologie Gmbh Process for increasing the energy input in electric arc furnaces
US4853206A (en) * 1986-05-02 1989-08-01 The Boc Group Plc Treatment of waste material

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE1258846B (de) * 1964-01-02 1968-01-18 Bayer Ag Verfahren zur thermischen Spaltung von Abfallschwefelsaeuren
US3661534A (en) * 1970-06-15 1972-05-09 Zink Co John Apparatus for sulfur recovery
US4102651A (en) * 1972-10-14 1978-07-25 Davy Powergas Gmbh Ultrasonic atomizer for waste sulfuric acid and use thereof in acid cracking furnaces
DE2506438C3 (de) * 1975-02-15 1979-04-26 Davy Powergas Gmbh, 5000 Koeln Verfahren zur thermischen Spaltung von Abfallschwefelsäure
SE465731B (sv) * 1990-02-07 1991-10-21 Kamyr Ab Utvinning av energi och kemikalier ur massaavlutar under exponering av laagfrekvent ljud
DE4101497A1 (de) * 1991-01-19 1992-07-23 Basf Ag Verfahren zur thermischen aufarbeitung ammoniumsulfathaltiger rueckstaende insbesondere ammoniumsulfathaltiger abwaesser
US5129335A (en) * 1991-04-18 1992-07-14 Union Carbide Industrial Gases Technology Corporation Fluid waste burner system
GB9127096D0 (en) * 1991-12-20 1992-02-19 Ici Plc Treatment of liquid waste material

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4062657A (en) * 1975-05-09 1977-12-13 Eisenwerk-Gesellschaft Maximilianshutte Mbh Method and apparatus for desulphurizing in the gasification of coal
US4853206A (en) * 1986-05-02 1989-08-01 The Boc Group Plc Treatment of waste material
US4827486A (en) * 1986-08-27 1989-05-02 Klockner Cra Technologie Gmbh Process for increasing the energy input in electric arc furnaces

Cited By (19)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20100055627A1 (en) * 2004-08-16 2010-03-04 Air Products And Chemicals, Inc. Burner And Method For Combusting Fuels
US8512033B2 (en) 2004-08-16 2013-08-20 Air Products And Chemicals, Inc. Fuel nozzle for reducing carbon build up
US20100096037A1 (en) * 2008-10-16 2010-04-22 Woodward Governor Company Multi-Tubular Fluid Transfer Conduit
US8205643B2 (en) * 2008-10-16 2012-06-26 Woodward, Inc. Multi-tubular fluid transfer conduit
US20150053297A1 (en) * 2012-04-02 2015-02-26 Parker-Hannifin Corporation Container wand assembly
CN103090400A (zh) * 2013-01-29 2013-05-08 苏州华威工程技术有限公司 废气、废水焚烧处理装置
CN103090400B (zh) * 2013-01-29 2015-02-11 苏州华威工程技术有限公司 废气、废水焚烧处理装置
JP2014202433A (ja) * 2013-04-05 2014-10-27 Jfeケミカル株式会社 硫黄用燃焼バーナおよびこれを備える燃焼炉並びに硫黄の燃焼方法
US20170179508A1 (en) * 2015-12-22 2017-06-22 Fuji Electric Co., Ltd. Fuel cell apparatus
CN107860002A (zh) * 2017-11-01 2018-03-30 上海盛靓节能科技发展有限公司 一种用于工业窑炉的增氧节能喷枪
CN108246210A (zh) * 2018-01-30 2018-07-06 浙江工业大学 一种新型高温裂解反应装置
CN108246210B (zh) * 2018-01-30 2023-08-08 浙江工业大学 一种高温裂解反应装置
US10865714B2 (en) 2018-03-22 2020-12-15 Woodward. Inc. Gas turbine engine fuel injector
US11840961B2 (en) 2018-03-22 2023-12-12 Woodward, Inc. Gas turbine engine fuel injector
US20220325827A1 (en) * 2019-09-03 2022-10-13 Oriental Recreational Products (Shanghai) Co., Ltd Water circulation pipeline, control box and massage water pool
US12169044B2 (en) * 2019-09-03 2024-12-17 Oriental Recreational Products (Shanghai) Co., Ltd Water circulation pipeline, control box and massage water pool
CN110953597A (zh) * 2019-11-21 2020-04-03 浙江浙能技术研究院有限公司 一种高硫废气富燃装置及能源化利用方法
CN111795386A (zh) * 2020-06-11 2020-10-20 哈尔滨博奥环境技术有限公司 一种带有酸性气和燃料气喷枪的复合燃烧系统
CN111795386B (zh) * 2020-06-11 2024-06-04 哈尔滨博奥环境技术有限公司 一种带有酸性气和燃料气喷枪的复合燃烧系统

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ATE287513T1 (de) 2005-02-15
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